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Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT

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ment of interest (e.g., <strong>the</strong> entire range). The model contains in<strong>for</strong>mation about<strong>the</strong> environment, including <strong>the</strong> initial location of owls, and a series of rulesgoverning births, deaths, and movements. These rules are used in a stochasticsimulation of births, deaths, and movements during a year. At <strong>the</strong> end of <strong>the</strong>year, <strong>the</strong> locations of all owls are again recorded, and <strong>the</strong>n <strong>the</strong>y are used <strong>for</strong><strong>the</strong> second year of <strong>the</strong> simulation. This process is repeated <strong>for</strong> as long a periodas <strong>the</strong> user desires. The model permits up to six cell types, three age classes,and two sexes, with possibly different demographic rates. The rules <strong>for</strong> movementsby juveniles and adults are flexible and permit simulation of a widevariety of behaviors. Additional details are contained in McKelvey (1991).The <strong>Recovery</strong> Team convened an advisory committee of biologists to providerecommendations on <strong>the</strong> use of <strong>the</strong> landscape model. The committee compileddata of value in determining <strong>the</strong> parameters required by <strong>the</strong> model and maderecommendations about certain structural changes. The advisory committeehas not finalized recommendations, but intends to do so during <strong>the</strong> coming fewmonths. Preliminary recommendations have been developed <strong>for</strong> habitat-specificproductivity, juvenile survival rates, and adult survival rates <strong>for</strong> Washingtonand Oregon west of <strong>the</strong> Pacific crest and north of <strong>the</strong> Klamath provinces. Themodel appears powerful, flexible, and capable of realistic simulations. Considerablework is needed, however, to make <strong>the</strong> model operational. The followingin<strong>for</strong>mation is of particular importance:1. Habitat specific productivity and survival.Preliminary estimates are available <strong>for</strong> portions of <strong>the</strong> range, but in o<strong>the</strong>rportions we do not have definitions <strong>for</strong> cell types. The needed in<strong>for</strong>mationcould be collected using two general approaches. First, home ranges ofbirds being monitored <strong>for</strong> productivity and adult survival should be assignedto cell types so that a sample <strong>for</strong> each type could be obtained. Second,intensive studies of transmittered birds should be made to improve ourunderstanding of habitat types that are used and avoided. Study shouldalso be made of <strong>the</strong> particular values to owls provided by each stand type.Much work of this sort has been done in western Oregon and Washington,but similar studies are needed (and in some cases are in progress) in environmentseast of <strong>the</strong> Cascades crest, in Cali<strong>for</strong>nia, and in <strong>the</strong> OregonKlamath province. Habitats of particular interest should be selected <strong>for</strong><strong>the</strong>se studies.2. Effects of habitat on movements by dispersing juveniles.This topic has received little study but is critical <strong>for</strong> <strong>the</strong> evaluation of <strong>the</strong>recommended DCA network. Intensive monitoring of dispersing juveniles isneeded to reveal how <strong>the</strong>ir movements and survivorship are affected by <strong>the</strong>configuration of habitat in <strong>the</strong> landscape <strong>the</strong>y pass through, how widely <strong>the</strong>ysearch <strong>for</strong> territories during dispersal, whe<strong>the</strong>r <strong>the</strong>y settle in <strong>the</strong> first availableplace, and how far <strong>the</strong>y travel if vacancies are not available. Closemonitoring of a relatively small number of birds (ra<strong>the</strong>r than occasionallocation of a larger sample) is needed. Monitoring such a sample of dispersingbirds, and analysis of <strong>the</strong> habitats and resident owls in <strong>the</strong>ir path, wouldprovide a far better basis than we have at present <strong>for</strong> deciding on <strong>the</strong> valuesof <strong>the</strong> movement parameters in <strong>the</strong> landscape model. Such studies might becarried out in <strong>the</strong> density areas where <strong>the</strong> locations of o<strong>the</strong>r owls are alreadywell known.3. Behavior of nonterritorial adultsNonterritorial adults may buffer <strong>the</strong> population against loss of breedingadults if <strong>the</strong> floaters rapidly fill vacancies (Franklin In Press). At present,267

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